|
The
Association for Better Land Husbandry Regd.
Charity 1025653 AN
ECOLOGICAL BACKGROUND TO
CONCEPTS OF LAND
HUSBANDRY by R G
Downes and PRINCIPLES OF
GOOD LAND HUSBANDRY by T F
Shaxson M G Douglas R G
Downes |
CONTENTS
An ecological background to concepts of land
husbandry
Principles of good land husbandry
Other readings
.oOo.
AN
ECOLOGICAL BACKGOUND
TO
CONCEPTS OF LAND HUSBANDRY
(Extracted
from Downes, 1982)
INTRODUCTION
"Unless there is a positive commitment by
the Government and people ... for looking after their resources for future
generations as well as the present, then conservation concepts become
meaningless.
*
"The most important requirement at present
is for everybody to be made to understand that soil conservation is more than
erosion control and that it is not just an agricultural problem. Soil conservation is really a matter of
applying the appropriate uses to different kinds of land.
*
TECHNICAL
CONSIDERATIONS FOR GOOD LAND USE
"Conservation is a man-made concept
concerned with how man relates to his land and uses its resources. The objective is to determine and put into
practice how he can satisfy his physical and aesthetic needs from the land
without spoiling its capability for continuing to satisfy those needs.
"To be successful, man must understand the
ecological dynamics of different kinds of land and use that knowledge to devise
non-destructive systems of land use and management for each kind of land. The knowledge of how land will react to
imposed changes is the basis for making decisions about land use and management
so as to maintain the capability for the chosen use.
*
"Land is the basic resource of a
nation. To provide for all of his
needs, man must use land for many purposes.
He needs land to produce food, fibre, timber and water, for urban and
industrial purposes, for transport by roads, railways and airports, for the
extraction of minerals and building materials, for distributing power by
transmission lines and pipelines and for the safe disposal of wastes. But he also needs land for non-productive
purposes: for recreation and enjoyment;
and land in its natural state to serve as reference areas and as habitat for
the vast array of species of plants and animals, a great repository of genetic
material that could be of value in the future.
"Apart from those uses needed for
subsistence, all other uses are of equal necessity although the priorities of
different communities for uses of land may change from time to time.
*
"Some uses of land such as agriculture are
flexible because that use does not preclude many other future uses and it is
easy to change to the other use. Some
uses such as urban and industrial uses and forest plantations are inflexible
because once the use is imposed it must continue for a long time. A use such as open space for recreation does
not affect the capability for other uses, but ones like open cut mining change
the nature of the land and preclude most options for future use.
*
"Uses such as scientific reserves and water
catchments are compatible with each other and the land can be used for both
purposes at the same time by multiple use;
other uses such as agriculture and scientific reserve are incompatible
and a choice must be made.
*
"Land varies from place to place in the
landscape. Different land has different
characteristics and different capabilities.
The character of the land in any place is determined by the particular
combination of the features of which it is composed: the topography, soil,
hydrology, fauna and flora and the climate in which it is located.
"The nature of the features and the
character of the land is the result of a long evolutionary period of
interaction between the features in the prevailing climate. Where the interactions have been the same in
the landscape, the same kind of land is to be found. Consequently the variations of land and the
spatial arrangement of different kinds of land in the landscape are not due to
chance but to different types of interactions.
These differences can be studied and explained and used to determine the
nature of the land, its capability for various kinds of use, the hazard of
using it for different purposes and the relationship and interaction between
the land occupying different situations in the landscape.
"In the natural state, land has a dynamic
equilibrium. Although it may appear to
be unchanging, the interactions are continuing. Within each kind of land there is a
community of plants and animals which, from among the species available, are
appropriate populations of those best able to live in association and competition
with each other under the prevailaing climatic, topographic, hydrologic and
soil conditions. The trend of the
interactions and the resulting succession of different species of plants and
animals is towards a maximum sustainable biological productivity attainable
from the available array of species.
*
"When man uses land for plant and animal
production he changes the natural systems because the existing maximum
sustainable biological productivity is either not sufficient or not what he
wants. Some kinds of land can be
changed without becoming unstable, but others in which the stability depends on
specially adapted plants, or a particular hydrologic balance or some other
special feature can easily become unstable.
Unless the imposed system of use and management incorporates precautions
for maintaining a new stability, land degradation occurs. Man has failed to understand that ecological
principles must be applied to devise
suitable stable systems of use and management for different kinds of land. Clearing land of its original vegetation,
cultivating, burning and introducing new species of plants and animals are
significant changes that can equal in their effect the rare catastrophic
changes during geological time that set off sequences of erosion and reshaping
of the topography. The altered
hydrology and the long periods when bare soil is exposed to the effects of sun,
wind and rain are the basic causes of land degradation.
"But land degradation is not always due to
changes made for agriculture. Badly
located urban development, badly sited roads, bad forest harvesting and a whole
range of man's activity can cause instability and degradation.
"Some people have sought a solution by
trying to correct land degradation after it has occurred. This is a negative approach which implies
that whenever land is used, degradation is an inevitable consequence which can
only be controlled. The ecological
approach to land use and soil conservation is much more positive. It is based on understanding the land, its
capability for use and the hazards that must be overcome when used for
different purposes. The objective is to
use land only for purposes within its capability by perceiving the potential
causes of instability and designing the system of use and management to
overcome them.
*
"Achieving soil conservation will require
good decisions by many people and not only those who are using the land. For this reason ecological principles can be
used to provide guidelines for decision making if land degradation is to be
avoided.
- Decisions should be made on the basis of
adequate information about the land, its character, its capability for
different uses, the hazards to be overcome when used for different purposes and
its relative suitability for the various available options for use.
- Decisions should be made on the basis that
different kinds of land have different potentialities for various uses, the
most valuable land being that eminently suitable for a number of uses.
- Land having the potential for many uses should,
as far as possible, be maintained under a flexible form of use to retain the
greatest possible range of options for the future.
- Multiple use of land should be used to the
greatest possible extent.
- Development of new land for production should
be in response to real social or physical need;
undeveloped land is the most flexible form of land use; it retains the widest possible range of
options to cater for future needs.
- Decisions to use land for particular purposes
should take into account not only the likely hazard of degration to that land
but also to other land.
- Before deciding about using land for a
particular purpose suitable management to prevent hazards must be available.
*
"The real problem is inappropriate systems
of land use. When land is cultivated
too much and develops a compaction layer, and it is left without vegetative
cover for far too long in each year and
the rotations have no provision for a restoration phase that will improve the
structure, organic matter and fertility, the land is vulnerable.
"The soil loses its structure, the
infiltration capacity is reduced, the chances of increased water flow across
bare soil is increased and soil erosion occurs more frequently.
"The emphasis on erosion and its control,
the erodibility of soils and permissible amounts of soil loss is a negative and
unsatisfactory attitude.
*
"... those using the land, making decisions
about its use or conducting research must develop a new attitude based on
ecological principles. They must
understand that any act of manipulating land produces reactions. These reactions must be perceived and taken
into account in managing and using the land if land degradation is to be
prevented.
"In future, land must be looked on as a
resource to be nurtured and used appropriately and not as a commodity to be
traded or as a raw material to be wasted by inappropriate use.
*
A
PHILOSOPHY ABOUT LAND AND ITS USE
"A better community attitude to land can
only come from the development of a philosophy about the land and its
significance
to the welfare of a community. Such a philosophy will engender a widespread
attitude that conforms with it.
"At present people in many countries have no
clear understanding about the nature of land, land use, soil conservation or
even about man's relation to the environment and his dependence on the land and
its productivity.
"While this confusion exists it is difficult
for any stated policy and objectives about land to emerge. The
acceptance of a philosophy based on ecological principles will be technically
correct and will provide the basis for suitable policy and objectives for
attaining good land use and preventing land degradation.
"Acceptance of the following statements
would serve as a suitable philosophy:
- The land is the basic resource of a nation and
its use and management in a manner that causes degradation or destruction is
undesirable because it affects the welfare of the whole community.
- Different kinds of land are dynamically
balanced ecological systems which will be degraded or destroyed if the system
of use and management imposed on them does not provide stability also.
- The kind and degree of manipulation that can be
imposed safely on any land system to provide for the wide variety of needs of
the community depends on the ecological characteristics of the system.
- The use of land should be based on an
understanding of its ecological characteristics, the limitations of its
capability and the need to obviate the hazards that would cause degradation if
submitted to some kinds of land use and management.
- The requirements of the community can be
satisfied only by submitting land to a
variety of uses required to
satisfy the different needs. Decisions
about the future development use and management of the land and its resources
should be made in an integrated and comprehensive way taking into account the
total needs of the community now and in the future, and making use of the land
and its associated water systems to the greatest possible extent for the uses
for which they are most suitable.
- Land having the potential for a wide range of
uses should be maintained in flexible forms of use as far as possible.
- In using land and its resources long term
advantage should be pursued, rather than short term expediency that will lead
to exploitation, degradation and finally destruction."
REFERENCE
DOWNES R G, 1982.
'Institution Building for Soil and Water Conservation in Brazil'. Consultant's report to Project
BRA/82/011. Rome: FAO (AGLS). pp.43.
(unpubd.)
see
also
DOWNES R G, 1971.
'Land, Land Use and Conservation',
in: Costin A B and Frith H J (eds.) 'Conservation'. Penguin Books (Australia).
.oOo.
PRINCIPLES
OF
GOOD LAND HUSBANDRY:
Achieving
conservation of land's productive potentials
"HUSBANDRY:
The business of a farmer: tillage : economical management: thrift. Old English: Husbonda - hus: a house; buandi: inhabiting, (pr.p. of Old Norse. bua:
to dwell."
(Chambers
20th Century Dictionary,
1983, p.613)
DEFINITION
Good land husbandry is the active process of
implementing and managing preferred systems of land use and production in such
ways that there will be increase - or, at worst, no loss - of productivity, of
stability or of usefulness for the chosen purpose;
also,
in particular situations
Existing uses or management may need to be
changed so as to halt rapid degradation and to return the land to a condition
where good husbandry can have fullest effect.
(derived
from Downes, 1982)
INTRODUCTION
The concept of 'husbandry' is widely understood
when applied to crops and animals in the sense of 'looking after them'. As a concept signifying active
understanding, management and improvement, it is equally applicable to
land. Crop husbandry, animal husbandry
and land husbandry all imply the following:
- Understanding the characteristics, potentials
and limitations of different types of plants, animals and land;
- Predicting the likely positive or negative
effects on their productive potentials resulting from a given change in
management, or of severe but uncommon events such as epidemic disease or severe
rainfall;
- Working out how they can be strengthened to
resist the negative effects of such events;
- Adopting systems of management that maintain
their productivity and usefulness;
- Improving their production in terms of quality
and quantity of output in a given time;
- The active and central role of the farmer as
manager and steward of the resource.
In the case of land, a primary concern is to
maintain its productive capabilities and to avoid their degradation. Land degradation may result from decline in
biological, chemical or physical attributes of the soil, such as decline in
organic activity, waterlogging, acidification, loss of porosity, and/or the
loss of soil particles, nutrients and runoff.
In some situations, loss of the voids in the soil
associated with loss of soil structure (degradation of the soil's architecture)
leads to increased resistance to root growth, less retention of soil moisture
in plant-available condition, and reduced infiltration-capacity and
permeability, all of which can lead to reductions in yields. Loss of plant nutrients - which are cycling
in the organic materials and processes of the ecosystems - through leaching,
wash-off and crop removal can cause rapid and significant declines in potential
soil fertility levels.
Accelerated erosional loss of soil particles,
organic materials and nutrients by wind or water is frequently a consequence
of decline of soil structure - especially within the top few millimetres of a
soil profile - rather than itself the primary cause of land degradation. Decline of soil structural conditions may be
caused by compaction, by pulverization, by collapse or by interstitial sealing
due to raindrop action. The resulting
accelerated runoff and erosion are foreseeable ecologic consequences of
inadequate husbandry of the land.
The keys to sustainability and replicability of
improved land use systems lie with land-users themselves. They are the ultimate decision-makers about
what is done on their lands from day to day, and their decisions affect the
well-being of the land. Small-farm
families are artists in survival in the various agro-ecologic and
socio-economic environments with which they are familiar. However, when they move to unfamiliar
environments their artistry may be of little avail at the outset when they know
little or nothing about the nature, systems, functioning, hazards, potentials
or limitations of their new environment.
Nevertheless, their latent skills, relevant local knowledge and varied
enthusiasms are major resources which in most situations have scarcely been
tapped, a failure which hinders success and sustainability of development
efforts.
Because the management of land is undertaken by
rural people, good land husbandry embraces both agro-ecologic and
socio-economic principles.
AGRO-ECOLOGIC PRINCIPLES
LAND FOR THE FUTURE
People in the future have a right to make use of
land which is in good condition. Types
of land for whose safe and sustainable use an adequate technology is not yet
available or feasible should wherever possible be left in an undisturbed natural
condition so as to leave all options open for a range of safe alternative uses
in later years. This indicates a
present need to concentrate plant nutrients, water, organic and inorganic
fertilizer materials, effort, and other productive resources into limited areas
('niches') of intensive land use in carefully-husbanded micro-environments
within larger units of land.
Of land being brought into use, or already in
use, as much as possible should be maintained under flexible types of use (of
which undisturbed natural vegetation is the most flexible type, whereas e.g.
permanent buildings or roads etc. would be a most inflexible type). This leaves a maximum number of options for
different uses in future from which others may still choose.
To the extent possible, multiple uses of a given
area of land should be favoured, so as to maintain as much as possible
elsewhere under undisturbed and flexible conditions with regard to the future.
Descriptions of the suitability of a given area
of land for different uses should always include definitions both of the
degradation hazards of the land itself and of the conservation-effectiveness of
the proposed forms of use and their management, so that hazards and husbandry can
be suitably counterbalanced in the planning of actions.
ACHIEVING CONSERVATION
Across a varied area of land, achieving
conservation requires that husbandry should be so adjusted to each homogeneous
sub-area that any rate of degradation is effectively minimised, and that no one
part 'wears out' or becomes unproductive more quickly than any other.
In situations where the present type of land use
is incompatible with apparent land-use capability but the use cannot be
changed, the management of that use should be improved - particularly in
terms of cover to the soil and the soil's architectural (structural) and
nutritional conditions - so as to increase the conservation-effectiveness of
current practices and thus to minimise the risks of degradation, of soil loss
and the concomitant uncovering of less-fertile subsurface soil materials on
which subsequent crops would have to be planted.
Skilled and appropriate management for production
- of croplands, pasturelands and woodlands - itself should achieve effective
conservation of the land's productivity and usefulness under the range of usual
climatic conditions of a given area.
Key factors are:
- The presence of adequate degrees of cover to
the soil (with respect to density, frequency, timing and duration);
- Optimum
conditions of soil architecture (with respect to grades and stability of
structural units, which are highly dependent on organic materials and organic
processes) for both the aeration of the soil and the infiltration and retention
of water on the one hand, and for good growth and functioning of roots on the
other;
- Provision of plant nutrients from organic
sources (supplemented as needed by those from inorganic sources) to at least
replace - or if necessary exceed - those lost by harvesting of plants,
leaching, and unavoidable runoff.
Where yields are unnecessarily low, increased
production of plant parts per unit area may on the one hand automatically
provide increased protective cover to the soil, and on the other hand increase
the transpiration of soil moisture and and thus contribute to temporary
improvement in the soil's moisture-storage capacity. Higher yields thus may contribute simultaneously
to both higher production, better conservation, and better stability of the
land-use system.
While good husbandry practices will provide
adequate protection within the expected range of normal climatic conditions,
additional specialised conservation practices - which are simple and effective,
and require little expense and labour for implementing - may be justified as
precautions against effects of less frequent, more severe events.
ROTATIONS AND SOIL RECUPERATION
To sustain productivity under agricultural
conditions in which tillage, compaction, erosion or other problems may damage
them, soils generally require regular periods of restorative management in the
cycles of agricultural use. The
development, restoration and maintenance of optimum chemical, physical and soil
moisture conditions for plant growth are strongly dependent on the presence of
organic materials and the activities of micro- and meso-organisms, preferably
coupled with the effects of the roots of living grasses and perhaps other
perennial plants during the recuperation break in each rotation.
DIVERSITY AND STABILITY
The more biologically diverse and complex is an
agricultural system, the more stable and sustainable it is likely to be in the
face of unpredictable vagaries of climate and of the market.
SOCIO-ECONOMIC
PRINCIPLES
FARMERS' DECISIONS
Farmers are primarily concerned with stable and
economic production, not with conservation of soil and water per se,
especially when this latter may entail physical work or investment of resources
which show little or no perceptible benefit.
Rural people make rational decisions within the
'envelope' which encompasses their circumstances, skills and resources. Improvements in land husbandry are more
likely to occur if the 'shape' of this envelope within which they make their
decisions is changed and enlarged, than if attempts are made to change their
rationality within an unaltered envelope.
Farmers will not amend what they are already familiar with unless they
perceive that recommended changes will be both workable in practice and
sufficiently beneficial to them in terms of their goals.
People are only likely to adopt recommendations
for improved husbandry practices to the extent that they judge that the
practices are able to:
- Stabilise or increase present output;
- Be economic;
- Confer other benefits which are important to
them; and/or
- Simultaneously release resources e.g. time,
energy, cash etc., for other actions or investments (which may or may not be
agricultural).
PARTICIPATING WITH FARM FAMILIES
In a given situation, suggestions for
improvements in land husbandry should be developed together with rural people,
using their knowledge, awareness of problems, analysis, insights, capacities,
skills, goals, aspirations, enthusiasms and priorities.
In most situations, the first step in provoking
or assisting change and improvement is to start from what people already know,
and to help them first to do better what they are already trying to
achieve. Building and strengthening
effective traditional or familiar techniques, systems and institutions is
likely to engender more interest and commitment than will the attempted
introduction of unfamiliar approaches or of actions which farmers perceive to
be unacceptably risky and/or of no real benefit.
Local knowledge, rationality and skills should be
respected, and enriched in appropriate
ways. Locally-acknowledged boundaries -
whether of a group's shared interests or of the land area at its disposal - may
be more significant than topographic or other geographical boundaries in
defining appropriate land areas for action.
Farm families' enthusiastic undertaking of new activities is
significantly more likely if they have fully participated in the
decision-making process that led up to such activities than if they had
been inadequately - or not at all - consulted. This participation will include:
- Identifying and ranking problems and
opportunities;
- Formulating and implementing appropriate courses
of action;
- Monitoring and evaluating the outcomes of these
decisions and actions.
Conservation of productivity and of soil can be
more acceptably achieved by stealth (that is, indirectly) - via improvements in
know-how, in farming systems management and output, which evidently help farm
families to achieve their goals - than by frontal attack only with specialised
conservation measures. Seen in another
way, where cover over the soil is excellent,
where the soil architecture is stable, porous and absorptive, where
plants have adequate nutrition, and yields are high, there is seldom need to
worry much about the risks of runoff, erosion, loss of water, organic matter
and nutrients, or of subsoil exposure.
CREDIBILITY OF ADVISERS
Credibility of advisers is essential to two-way
transfer of information, and must be earned, not assumed, from the
outset. Without it, there will not be
among farmers the necessary receptivity and willingness to consider new
viewpoints and ideas which their advisers might suggest.
The credibility of technical advisers is enhanced
when the ranking of problems to be addressed is that accorded by the household
or community in the light of the knowledge its members have about the possible
solutions, and where allowance is made for the fact that people's priorities
and their ranking may change with time and circumstance.
In a participatory 'bottom-up' approach, technical
advisers in day-to-day contact with rural people need to be able to act more as catalysts,
facilitators and sources of new skills and information for discussion, rather
than as bearers of messages from higher authority.
In situations of small-scale and subsistence
agriculture at least, the sequence in which improvements are introduced into
farmers' discussions may be at least as important, in attracting farmers'
attention, as the nature of the suggested improvements,
Many of the problems and possibilities that rural
people encounter are interlinked and may cross-cut more than one conventional
technical discipline. Staff of agencies
offering them advice are more likely to note a positive response where this
aspect is acknowledged by providing technical advice within an 'ecology of
disciplines' rather than as an assortment of apparently unrelated bits of
information.
It is not usually desirable or possible to 'push
farmers around' - in respect of either
the types of production they follow or the places in which they undertake them
on the landscape - merely in the interest of getting the physical arrangement
of land uses to match technical maps of assumed 'land use capability'.
Outline: Some of the key features of new thinking about
land husbandry are set out in the two Tables which follow.
.oOo.
BACKGROUND
READINGS
(as at 1997)
DOUGLAS M G, 1994. Sustainable Use of Agricultural Soils : A
Review of the Prerequisites for Success or Failure. Berne(Switz.) : Univ. Berne/Inst. Geog. 162pp.
ROOSE E, 1993.
Water and Soil Fertility Management : A New Approach to Fight Erosion
and Improve Land Productivity. in: Acceptance of Soil and Water Conservation =
vol. 3 of Topics in Applied Resource Management (eds. E Baum, P Wolff, M A
Zobisch). Witzenhausen (Ger.): German
Inst. for Tropical and Subtropical Agriculture (DITSL). ISBN 3-9801686-4-6. 129-164.
See also (in French):
ROOSE E, 1994. Introduction a la
Gestion Conservatoire de l'Eau, de la Biomasse et de la Fertilite des Sols
(GCES). Bulletin Pedologique de la FAO
70. Rome: FAO. ISBN 92-5-203451-X. 420pp.
SHAXSON T F, 1993. Conservation-Effectiveness of
Farmers' Actions : A Criterion of Good Land Husbandry. in: Acceptance of Soil and Water Conservation
= vol. 3 of Topics in Applied Resource Management (eds. E Baum, P Wolff, M A
Zobisch). Witzenhausen (Ger.): German
Inst. for Tropical and Subtropical Agriculture (DITLS). ISBN 3-9801686-4-6. 103-127.
SHAXSON T F, HUDSON N W, SANDERS D W, ROOSE E,
MOLDENHAUER W C, 1989. Land Husbandry :
A Framework for Soil and Water Conservation.
Ankeny(USA): Soil & Water Cons. Soc.
ISBN 0-935734-20-1. 64pp.
.oOo.
continue
▼
BETTER LAND HUSBANDRY - ALTERING SOME TECHNICAL
PERSPECTIVES
|
NEWER VIEW |
OLDER VIEW |
|
1. Chief causes for concern are (a) decline of land's in-situ
productive potentials, and (b) insufficiency of soil moisture. |
1a. The primary cause for concern was with quantities
lost of soil particles and water. |
|
2. Improving and managing soil to ensure optimum
rainwater absorption and retention will have more sure and widespread effects
on plant production than only constructing physical cross-slope works to
catch or direct runoff water and soil already on the move. |
2a. It was commonly assumed that cross-slope physical
conservation works would result in significant increases in yield, by holding
back soil, water and nutrients in narrow bands across the slope. |
|
3. Accelerated runoff and erosion are foreseeable
ecological processes, and consequences of other aspects of land
degradation |
3a. Accelerated runoff and erosion were visualised as
primary active causes of land degradation. |
|
4. Post-erosion yields at any site after erosion are
closely related to the quality of soil which still remains in situ. |
4a. It wass generally assumed that decline in yields
post-erosion could be related closely to quantities of water, soil particles
and plant nutrients lost in the erosion process. |
|
5. Rainfall's erosivity can be minimised by breaking
the force of large raindrops by ensuring
some form of cover over the soil surface. |
5a. Erosivity of rainfall was usually implicitly
assumed to be an unalterable feature of each rain event. |
|
6. Soil's erodibility is increased or diminished over
time by effects of management of the soil. |
6a. Erodibility of a soil series was assumed to be an inherent characteristic of that
series. |
|
7. More intensive use of land at a particular site -
such that it (a) improves soil architectural conditions by favouring
soil-organic transformations and minimising tillage-damage, and (b) increases
density, duration and frequency of cover over the soil - can improve rather
than diminish conservation-effectiveness of the particular use. |
7a. If at a particular site the land land use was 'too
intensive' for the Land Use Capability classification of that site, it was
recommended to reduce the land use intensity until it matched that permitted
for that Class. |
|
8. Increased production of plant parts - with improvements in soil architectural
conditions, and in the amounts of cover over the soil - is an effective way
of achieving conservation of water and soil as a consequence of better
husbandry within the farm production system |
8a. It was usually insisted that soil conservation be
done/implemented before yields could rise. |
|
9. Because the land system is dynamic, maintaining its
capacity to continue producing what we want requires its active and
conservation-effective management over time, at the same time as any re-allocations
of land uses and imposition of any necessary physical works. |
9a. It was implied that land would be least subject to
erosion when its uses were allocated across the landscape in accordance with
the maps of 'Land Use Capability Classification', and treated with types and
layouts of physical and biological conservation measures. |
|
10. Solving problems of low productivity and of
erosion and runoff requires an inter-disciplinary approach to match the
inter-relatedness of the problems' causes. etc. |
10a. It was assumed that soil conservation requiresd a
mono-disciplinary specialist approach independent of other specialisations, and needing
separate institutional arrangements.
etc. |
BETTER
LAND HUSBANDRY - ALTERING SOME SOCIO-ECONOMIC PERSPECTIVES.
|
|
|
|
NEWER VIEW |
OLDER VIEW |
|
11. Farm families have their own observations and
perceptions about land degradation, and other views of the reality than those
of non-farm agriculturists/specialists: they should be allowed to judge what
is best in their situation. |
11a. Specialists' perceptions of the land degradation problems
and solutions were presumed to be the correct ones: outsiders would judge
what is best. |
|
12. The rural community, and the development of its
abilities to manage its own
environment, is the most appropriate focus of development assistance. |
12a. Land conservation, production and economic
efficiency were usually proposed as the primary foci for development
assistance. |
|
13. Resource-poor small farmers have considerable
knowledge about their environments, and make rational decisions about
allocation of their resources within the 'envelopes' of constraints within
which they make those decisions; the
challenge is to lessen constraints and improve the shape of the 'envelope'. |
13a. It was implicitly, or even explicitly, assumed
that small resource-poor farmers are by nature conservative, irrational and
ignorant of good land use; the task was
to change farmers' rationality. |
|
14. Rural families ultimately decide what will be done
on the land, and whether it would be in their interests to change according
to recommendations; resource-poor
small farmers are more vitally concerned than any outsider to maintain their
lands' productivity in both the short and long term. |
14a. Governments assumed that they decide what would
be done on the land, as they assumed they had a greater long-term concern to
maintain productivity and halt land degradation than do small farmers with
(supposedly) short-term time-horizons. |
|
15. To get conservation-effective agriculture
improved, it is important to start from where people are now, assist them to
do better what they are already trying to do, and remove constraints that
inhibit their doing better. |
15a. Adoption of recommended changes and innovations were
promoted as being essential for getting agriculture moving. |
|
16. A community, and the land it occupies and uses, is
the optimum focus for village planning, and for integrating inputs of various
'disciplines'. |
16a. The topographic catchment/watershed, with the
people it contains, was generally stated to be the logically optimum unit for
programme planning, and for demonstrating the effects of technical
recommendations.. |
|
17. 'Participation' signifies technical advisers
participating with farm families in helping people to identify and rank their
most important problems, to decide what do about them, to implement decided
actions, and to monitor the outcomes. |
17a. 'Participation' was commonly taken to mean 'the
people participating in implementing plans', devised by outsiders, which were
considered good for them. |
|
18. Advisory workers should be promoters of dialogue
and of two-way information-transfer, catalysts of interactions, and
facilitators of interchange and of farmers' well-informed actions |
18a. Extension workers were trained as demonstrators and one-way transmitters of
information to farm families, in a process of 'transfer of technology'. |
|
19. Until they have proved themselves to the
satisfaction of individual farmers, technical advisers have very low
credibility at the outset of their interactions with farm families. etc. |
19a. Technical advisers armed with scientific
knowledge assumed themselves to be 100% credible from the outset. etc |
[unedited transformation from
WP to ms/WORD from diskette 97.4:ECOLGLHc:10.6.97]
For
information about
the former Association
for Better Land Husbandry (1992-2002)
please
contact
Mr
T F Shaxson,
formerly
Hon. Chairman,
Greensbridge,
Sackville
Street,
Winterborne
Kingston,
Dorset DT11 9BJ,
England
FShaxson@aol.com
The
Association was a UK-Registered Charity, no. 1025653
.oOo.
This paper - as Paper P1-1 in ‘Proceedings
of WASWC’ - and others of a similar nature in the broad field of ‘soil and
water conservation’, are posted on the website www.waswc.org,
which is operated by the
World Association of Soil and
Water Conservation.
(Original
97.4:ECOGLHc.lh:10.6.97)
D/msw/ablhbklts/ECOGLHdii-w
: 4.8.06